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Measurement of air kerma rate and ambient dose equivalent rate using the G(E) function with hemispherical CdZnTe detector

NUCLEAR ELECTRONICS AND INSTRUMENTATION

Measurement of air kerma rate and ambient dose equivalent rate using the G(E) function with hemispherical CdZnTe detector

Ping Huang
Nuclear Science and TechniquesVol.29, No.3Article number 35Published in print 01 Mar 2018Available online 19 Feb 2018
49803

Since the room-temperature detector CdZnTe (CZT) has advantages in terms of detection efficiency, energy resolution, and size, it has been extensively used to detect X-rays and gamma-rays. So far, nuclear radiation detectors such as cerium chloride doped with lanthanum bromide (LaBr3 (Ce)), thallium doped with cesium iodide (CsI (Tl)), thallium doped with sodium iodide (NaI (Tl)), and high-purity germanium (HPGe) primarily use the spectroscopy - dose rate function (G (E)) to achieve the accurate measurement of air kerma rate (K˙a) and ambient dose equivalent rate (H˙*(10)). However, the spectroscopy-dose rate function has been rarely measured for a CZT detector. In this study, we performed spectrum measurement using a hemispherical CZT detector in a radiation protection standards laboratory. The spectroscopy - dose rate function G(E) of the CZT detector was calculated using the least-squares method combined with the standard dose rate at the measurement position. The results showed that the hemispherical CZT detector could complete the measurement of air kerma rate (K˙a) and ambient dose equivalent rate (H˙*(10)) by using the G (E) function at energies between 48 keV and 1.25 MeV, and the relative intrinsic errors were, respectively, controlled within ± 2. 3% and ± 2. 1%.

CdZnTeSpectroscopy - dose rate G(E) functionAir kerma rateAmbient dose equivalent rateRelative intrinsic error

1 Introduction

At present, pulse-counting detectors such as the Geiger Müller (GM) tube, silicon p-i-n photodiode (Si-PIN), silicon photomultiplier (SiPM), plastic scintillator detector (PSD), cerium chloride doped with lanthanum bromide (LaBr3 (Ce)), thallium doped with cesium iodide (CsI (Tl)), thallium doped with sodium iodide (NaI (Tl)), and high-purity germanium (HPGe) can be used to measure the air kerma rate or ambient dose equivalent rate. However, it is difficult to form the equilibrium condition of charged particles with the detectors described above because the atomic coefficients of the detectors are higher than those of the tissue materials. Therefore,the photon energy response of the above-mentioned detectors is not consistent within the energy range from 48 keV to 1.25 MeV. Consequently, the measurement accuracy of the dose rate is limited. If the photon energy response of the above-described detectors is corrected, it is possible to replace the ionization chamber detector. At present, in addition to the special requirements on the instrument in terms of size and power consumption (e.g., electronic personal dosimeters (EPD)), the energy spectrum of the pulse-counting detector is mainly obtained by a multichannel pulse-height analyzer. In addition, spectrum measurement data can be used not only for the qualitative and quantitative analysis of element material, but also to calculate the air kerma rate (K˙a) and ambient dose equivalent rate (H˙*(10)).

The accurate measurement of dose rate using the energy spectrum is mainly performed by adopting the spectroscopy - dose rate function G (E) method. There are three methods for solving the G(E) function: the numerical method, Monte Carlo simulation with the calculation of the detector response matrix (DRM), and the method of measuring the spectrum in a standard radiation field.

The numerical calculation method uses the basic principle of interaction between radiation and matter, and the spectrum-formation mechanism of the detector is usually simplified. The numerical calculation mainly considers the impact of the peak area and Compton platform. The Compton platform is generally described using a rectangular distribution function [1]. The numerical method involves the attenuation cross-sectional data of the photoelectric effect and Compton effect of the filter material and the detector, but it usually ignores the influence of the electronic measuring system and the materials around the detector. Because the physical parameters of different types of detectors are different, the application software of the numerical calculation method is not universal. At the same time, owing to the simplification of the spectrum-formation mechanism, the accuracy of the calculation results is limited.

In the calculation method using the Monte Carlo simulation, the DRM is first simulated with a selected interval in a certain energy range, following which the DRM is inverted. Discrete values of G (E) can be obtained by multiplying the inverse DRM matrix with the quotient between the dose rate and the fluence rate at each monoenergetic condition [2-5]. The full G(E) can be determined by polynomial fitting of the discrete values of G(E) within a certain energy range [6-9]. Research on this method in the literature [8, 9], did not study the change in FWHM of the detector with the energy, the selection of dimensions of the DRM, and the ill-posed problems of the inverse DRM matrix. Furthermore, the steps in the Monte Carlo simulation for calculating the DRM are relatively complex and time-consuming.

The measurement of the spectrum in a standard laboratory combined with the least-squares method can also be applied to calculate G (E) [10, 11]. The dose rate of the radiation field can be obtained using theoretical calculation by a known activity point source at a distance, or it can be measured by a standard spherical ionization chamber. According to related papers [10, 11], G (E) can be described by a polynomial expression for the power of the natural logarithm, and it can be solved using the least-squares method. Compared with the previous method, this method can perform fast calculation, and has some common general features.

In recent years, relevant research on the spectroscopy - dose rate function G (E) was mainly focused on NaI (TI), HPGe, CsI (Tl), and LaBr3 (Ce) nuclear radiation detectors [12-15], and studies on the CZT detector are relatively few in number. Since the CZT semiconductor detector has a high detection efficiency, has a small size,is easy to use, and works at room temperature, it can be used for X-ray and gamma-ray imaging, X-ray fluorescence analysis, airport security and detection ports, astrophysics, X-ray radiography in industrial applications, chromatography, and other prospective applications [16-19]. CZT detectors are usually of the planar type, trapping electrode type, co-planar gate type, capacitive Frisch grid type, pixel type, and hemispherical structure type. Hemispherical and co-planar gate CZT detectors can partially replace NaI (Tl) detectors at the environmental level, or they can be used at the measurement range of low-level radiation. However, so far, few spectroscopy - dose rate methods of CZT detectors have been reported. For these reasons, the present study utilized a hemispherical CZT detector at room temperature as a test subject to measure the spectrum in a standard radiation protection field, and used the least-squares method to calculate G (E) to verify the relative inherent error of the air kerma rate (K˙a) and ambient dose equivalent rate (H˙*(10)).

2 Method for calculating G(E)

ϕ(E0) is defined as the fluence rate of energy E0, and M(E) is the spectrum measured by the CZT detector in unit time. EminEEmax, where Emin is the minimum detectable energy and Emax is the maximum detectable energy. R(E,E0) is the response function of the CZT detector, which represents an X-ray or gamma-ray of energy E0 that deposits an energy E into the CZT detector. M(E) can be expressed by Eq. (1):

M(E)=EminEmaxR(E,E0)ϕ(E0)dE0. (1)

It is assumed that the fluence rate ϕ(E0) can generate a dose rate D0 at the detector position, where the units of the dose rate can be μGy/h or μSv/h. D0 can be expressed by Eq. (2), where h(E0) is the fluence - dose conversion factor.

D0=ϕ(E0)h(E0). (2)

When using the spectroscopy - dose rate function G(E) to measure the dose rate, Eq. (3) can be obtained.

D0/ϕ(E0)=h(E0)=EminEmaxR(E,E0)G(E)dE. (3)

Eq. (3) is for the case of monoenergetic radiation, and in multi-energy radiation conditions, the dose rate can be represented by Eq. (4).

D=iϕ(Ei)h(Ei)=iϕ(Ei)EminEmaxR(E,Ei)G(E)dE=EminEmax[iϕ(Ei)R(E,Ei)]G(E)dE=EminEmaxM(Ei)G(Ei)dE. (4)

Eq. (4) can be changed to Eq. (5) by using the channel number N, where N=1024.

D=i=1NM(Ei)G(Ei). (5)

According to related papers [10, 11], G (E) can be expressed by Eq. (6). In Eq. (6), A(K) is a parameter, M is a constant, and Kmax is the number of terms. G(E) can be solved using the least-squares method by measuring the spectrum in a standard radiation field [10-13].

G(E)=K=1KmaxA(K)(log(E))KM1. (6)

3 Detector measurement system

A schematic diagram of the CdZnTe (CZT) detector system is shown in Fig. 1, which includes the CZT detector, charge-sensitive amplifiers, proportional amplifiers, high-speed analog-to-digital converter (ADC), field-programmable gate array (FPGA), micro control unit (MCU), and personal computer (PC) software. The hemispherical detector has an effective volume of 5.0 mm × 5.0 mm × 2.5 mm. Charge-sensitive amplifiers change the current signal into a voltage signal, and proportional amplifiers further amplify the voltage signal to improve the signal-to-noise ration. A pulse waveform is sampled by the high-speed ADC and shaped by the FPGA using the digital trapezoidal method. The pulse amplitude of the signal is extracted, and uploaded to the computer by universal serial bus (USB) for dose-rate calculation.

Fig. 1.
(Color online) Schematic diagram of the CZT detector system
pic

Fig. 2 shows the measurement system of the CZT detector. The detector module consisted of the CZT detector, charge-sensitive amplifier, and proportional amplifier, it is shielded against light and electromagnetic radiation by aluminum, and it uses a multi-core shielded cable for power supply and signal transmission.

Fig. 2.
(Color online) Measurement system of the CZT detector
pic

4 RESULTS AND DISCUSSION

The CdZnTe (CZT) detector system obtains the spectrum in the X-ray, and 137Cs, and 60Co radiation protection standard laboratory. The X-ray radiation field uses the lower air kerma rate spectrum series recommended by ISO, and the tube voltages were 55 kV, 70 kV, 100 kV, 125 kV, and 170 kV. The standard dose rate in the X-ray radiation field can be obtained using the ball-type ionization chamber of PTW Freiburg GmbH (Table 1). Since the PTW ionization chamber can usually measure air kerma rate (μ Gy/h), but through the recommended conversion factor [20, 21], the air kerma rate can be converted to the ambient dose equivalent rate (μSv/h). The CZT detector measured the air kerma rate (K˙a) and ambient dose equivalent rate (H˙*(10)) in the standard laboratory under the same conditions.

Table 1.
Radiation qualities used in radiation protection
  Tube voltage Tube current Additional filtration Distance (m) Mean energy (keV) (K˙a) (μGy/h) (H˙*(10)) (μSv/h)
  (kV) (mA) (mm)
      Al Cu Pb Sn        
Low exposure rate 55 0.25 4.0 1.00 / / 3.0 48.0 28.90 46.24
  70 0.25 4.0 1.96 / / 3.0 60.0 29.05 50.26
  100 0.50 4.0 0.20 / 2.08 3.0 87.0 27.24 46.04
  125 0.50 4.0 / / 4.00 3.0 109.0 36.29 58.43
spectrum 170 0.50 4.0 2.23 1.50 1.50 3.0 148.0 34.16 50.90
Isotope 137Cs           1.0 661.6 825.67 998.40
source 60Co           1.0 1250.0 4730.40 5487.26
Show more

Fig. 3 shows the spectra measured by the CZT detector in the radiation protection standard laboratory. The measurement time of each spectrum was two minutes, and each spectrum is normalized to the maximum count value. The detection efficiency (CPS/(μGy/h)) of CZT at 55 kV, 70 kV, 100 kV, 125 kV, 170 kV137Cs, and 60Co conditions were 187.9, 247.9, 226.8, 157.3, 82.4, 4.5, and 1.9, respectively. The above result makes the CZT detector similar to thallium-doped sodium iodide (NaI (TI)), high-purity germanium (HPGe), cerium chloride doped with lanthanum bromide (LaBr3 (Ce)), and thallium-doped cesium iodide (CsI (Tl)), and the energy response in the low energy range is higher compared with that in the high-energy range.

Fig. 3.
(Color online) Spectra measured by the CZT detector in the standard radiation field
pic

The use of Eq. (5) can solve the above problems. The coefficients A (K) of G (E) of Eq. (6) were solved using the least-square method [10, 11]. In Eq. (6), the K value is generally in the range between 8 and 14. The optimal G (E) was found by the application program when K was 12 and M was 0. When the K value is equal to 12, the coefficient A (K) of G (E) was calculated, as listed in Table 2, and the G (E) functions of air kerma rate and ambient dose equivalent rate are shown in Fig. 5 and Fig. 6, respectively.

Table 2.
The coefficients A(K) of G (E)
A(1) A(2) A(3) A(4) A(5) A(6) A(7) A(8) A(9) A(10) A(11) A(12)
Calculated A(K) for K˙a
0.000157 0.000311 0.000571 0.000921 0.001188 0.000929 -0.000250 -0.001239 0.000876 -0.000239 0.000030 -0.0000014
Calculated A(K) for H˙*(10)
0.000195 0.000389 0.000717 0.001163 0.001509 0.001192 -0.000300 -0.001574 0.001106 -0.000302 0.000038 -0.0000018
Show more
Fig. 5.
G (E) for H˙*(10)
pic
Fig. 6.
Measured and converted energy spectra for 137Cs; the energy spectrum for counts (top) and energy spectra converted into the ambient dose equivalent rate (bottom)
pic

As can be seen from Fig. 4 and Fig. 5, G (E) values change with the detected photon energy. The channel count value multiplied with G (E) can cancel the high response at low energy and low response at high energy. The principle of the method is to introduce a weighting factor according to energy deposition in the CZT detector, which makes the dose-rate measurement more accurate in the energy range of 48 keV - 1.25 MeV. At the same time, by using G (E), we can also calculate the dose rate at the segment where the energy is proportional to the total dose rate. Fig. 6 shows examples for the measurement of the spectrum with and without the use of G (E). In Fig. 6, the peak area of dose rate of 137Cs is 36% proportional to the total dose rate.

Fig. 4.
G (E) for K˙a
pic

Table 3 lists the measured values of Fig. 4 and Fig. 5 after using G (E). The relative intrinsic error of the air kerma dose rate (K˙a) and ambient dose equivalent rate (H˙*(10)) are, respectively, controlled within ± 2. 3% and ± 2. 1%.

Table 3.
G (E) used to measure (K˙a) and (H˙*(10))
Mean energy (keV) Standard value of (K˙a) (μ Gy/h) Measured values (μGy/h) Relative intrinsic error (%) Standard value of (H˙*(10)) (μSv/h) Measured values (μSv/h) Relative intrinsic error (%)
48.0 28.90 29.13 0.81 46.24 46.59 0.75
60.0 29.05 28.67 -1.32 50.26 49.59 -1.32
87.0 27.24 27.77 1.95 46.04 46.92 1.91
109.0 36.29 35.47 -2.25 58.43 57.20 -2.11
148.0 34.16 34.55 1.15 50.90 51.41 0.99
661.6 825.67 817.51 -0.99 998.40 991.47 -0.69
1250.0 4730.40 4754.85 0.52 5487.26 5506.39 0.35
Show more

Fig. 7 uses the total counting method and G (E) of air kerma rate to compute the photon energy response of the CZT detector (both normalized to 137Cs). The energy response of the air kerma rate after correction (normalized to 137Cs) is between 0.99 and 1.03 in the energy range of 48 keV - 1.25 MeV.

Fig. 7.
Energy response of K˙a for the CZT detector
pic

Fig. 8 uses the total counting method and the ambient dose equivalent rate G (E) function method to compute the photon energy response of the CZT detector (both normalized to 137Cs). The energy response of the ambient dose equivalent rate after correction (normalized to 137Cs) is between 0.98 and 1.03 in the energy range of 48 keV - 1.25 MeV.

Fig. 8.
Energy response of H˙*(10) for the CZT detector
pic

As shown in Fig. 7 and Fig. 8, for both the air kerma rate and ambient dose equivalent rate, the spectroscopy - dose rate function G (E) can effectively correct the energy response of the CZT detector. After using the G (E) of the K˙a and H˙*(10), the energy response curves are approximated to a horizontal line. The accuracy of dose-rate measurement of the CZT detector is greatly improved after using G (E) in the energy range of 48 keV - 1.25 MeV.

5 Conclusion

Spectrum measurement was performed using a hemispherical CdZnTe (CZT) detector under the conditions of the X-ray and the isotope 137Cs, 60Co radiation protection standards laboratory. The spectroscopy - dose rate function G (E) of air kerma rate and ambient dose equivalent rate could be obtained using the least-squares method. With the CZT detector using G (E) to measure the dose-rate parameter in the energy range of 48 keV - 1.25 MeV, the relative intrinsic error of air kerma dose rate and ambient dose equivalent rate were, respectively, controlled within ± 2. 3% and ±2. 1%, which are far beyond the ±30% requirement of the national standards. Spectrum measurement combined with the least- squares method to calculate G (E) has the advantages of easy programming, fast calculation, and wide range of application. The use of the hemispherical CZT detector to perform more accurate dose rate measurements with G (E) has practical application value.

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